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Anthemis cotula

Anthemis cotula, commonly known as stinking , mayweed, or dog , is an annual in the family characterized by its erect, branching stems growing 15–80 cm tall, finely dissected pinnate leaves that emit a strong, unpleasant when crushed, and solitary daisy-like flower heads with ray florets surrounding a disk. Native to the Mediterranean region and , A. cotula has been widely introduced to other continents, including , where it is now naturalized and considered an invasive in disturbed habitats such as roadsides, fields, areas, and arable lands. It thrives in a variety of types, including sandy, loamy, or clay soils, and germinates readily in response to soil disturbance, light exposure, and cool temperatures, often completing its from to autumn. Ecologically, it acts as a competitive that can reduce crop yields, particularly in like peas, by interfering with establishment and harboring pests, though it also serves as a minor nectar source for pollinators. Historically, A. cotula has seen limited traditional uses, such as a agent in some cultures or an due to its volatile oils, but it is primarily noted for its toxicity, causing skin irritation, allergic in humans, and symptoms like and in and pets upon ingestion. Its management as a involves cultural practices, herbicides, and prevention of to mitigate agricultural and ecological impacts.

Taxonomy

Classification

Anthemis cotula belongs to the kingdom Plantae, phylum Tracheophyta, class Magnoliopsida, order Asterales, family Asteraceae, genus Anthemis, and species A. cotula. Within the family Asteraceae, it is placed in tribe Anthemideae and subtribe Anthemidinae, a grouping characterized by shared morphological traits such as the presence of paleae on the receptacle and specific pollen morphology known as the "Anthemis-type." The classification of Anthemis cotula in the genus Anthemis has been supported by both morphological and molecular evidence, distinguishing it from closely related genera such as Matricaria and Tripleurospermum, which were historically considered in broader complexes due to similarities in structure and chemical profiles. Early classifications relied on carpological features, like morphology, and pollen characteristics, while modern revisions incorporate nuclear (nrDNA ITS) and (cpDNA ndhF) sequences that confirm the of subtribe Anthemidinae and position the genus Anthemis (subtribe Anthemidinae) closely related to subtribe Matricariinae, including Matricaria, within the Eurasian-Mediterranean clade of tribe . These molecular analyses have refined the boundaries of Anthemis, incorporating species previously debated in placement based on tetrasporic embryo sac development shared with Tripleurospermum. The species was first formally described by in in 1753, based on material from ruderal habitats. The lectotype, designated by Z. Yavin in 1970, is a specimen collected by Gerber without locality data, housed in the Linnaean as LINN 1016.16. This type material anchors the species' identity amid historical taxonomic revisions in the .

Etymology and synonyms

The genus name derives from the Greek word anthēmon, meaning "flower," alluding to the daisy-like inflorescences characteristic of the genus. The specific epithet cotula is a form of the Greek kotylē, referring to a "small cup," which describes the cup-shaped receptacle of the flower heads or the hollow at the base of the leaves. Over time, Anthemis cotula has undergone several nomenclatural changes due to shifts in generic circumscriptions within the family, leading to multiple synonyms. Accepted synonyms include Anthemis foetida Lam., Chamaemelum cotula (L.) All., and Maruta cotula (L.) ., reflecting past placements in genera like Chamaemelum and Maruta based on morphological interpretations. Common names for Anthemis cotula often highlight its pungent and weedy nature, such as stinking chamomile, dog fennel, and mayweed, which are widely used in and . In the United Kingdom, regional variations include pig-sty daisy and stinking mayweed, emphasizing its association with disturbed or unkempt areas.

Description

Morphology

Anthemis cotula is an annual herb typically growing 10–90 cm tall, with an erect or ascending that is often branched from the base or distally. The plant is glabrous to sparsely hairy, featuring glandular trichomes that release a strong, unpleasant when crushed. The stems are green, sometimes red-tinged or purplish, striate, and usually erect, branching throughout or mostly in the upper portions, with sparse strigose hairs or glabrescent surfaces. Leaves are alternate, 20–55 mm long and 15–30 mm wide, 1–2-pinnatisect or pinnatifid into linear segments 0.5–2 mm wide, and mostly glabrous with an aromatic scent when handled. The consists of solitary terminal heads, 15–30 mm in diameter, borne on peduncles 2–15 cm long. Involucral bracts are imbricate in 3–5 series, 5–9 mm across, with outer bracts green and brownish or scarious margins, often sparsely villous or arachnose. Ray florets number 10–20, are white, strap-shaped, and 5–15 mm long, while the numerous disk florets are yellow and tubular, 2–2.5 mm long. Fruits are achene-like cypselae, 1.3–2.1 mm long, with 10+ longitudinal tuberculate ribs, lacking a pappus, though a small remnant may be present at the .

Reproduction and life cycle

Anthemis cotula is an annual herb that completes its within one , functioning as either a winter annual or summer annual depending on environmental conditions. In cooler climates, seeds germinate in , forming frost-hardy rosettes that overwinter and resume growth in early spring; in warmer regions, germination occurs primarily in spring. The plant bolts in spring, producing upright stems that reach heights of 15–60 cm, followed by flowering from May to October, with peak bloom in June–July. After seed set, the plant senesces and dies, relying solely on propagation without . Reproduction in A. cotula is primarily sexual, occurring through facilitated by pollinators such as hoverflies (Syrphidae), bees, and other Diptera, though the is strongly self-incompatible with rates below 10%. The flower heads, consisting of white ray florets and yellow disc florets, attract these pollinators to promote cross-pollination, enhancing . Each mature produces numerous capitula, with an average of 50–75 seeds per head and up to 120 in larger ones; a single plant can yield thousands to over 27,000 seeds, contributing to its prolific output. Seeds of A. cotula exhibit innate , requiring pericarp degradation by soil microorganisms to initiate , which is further stimulated by exposure, alternating temperatures (day 20–30°C, night 0–10°C), and presence. occurs over a broad range of 5–30°C, with optimal rates at 20°C, allowing in fall, , or occasionally summer. Viability persists in for extended periods, maintaining over 50% after 11 years and approximately 6% after the same duration under conditions. Dispersal happens primarily through wind over short distances or adhesion to fur and clothing, facilitating local spread.

Distribution and habitat

Native range

Anthemis cotula is native to the , with its primary distribution spanning from the northward to , including , , and , and Western Asia encompassing and the region up to . This range reflects its adaptation to the temperate biome, where it has been documented since . The species was first formally described by in his in 1753, based on European specimens collected from ruderal habitats. Archaeobotanical records confirm its long-standing presence in ancient European floras, with seeds identified in Mid sites and increasing in frequency during the period, particularly in association with agricultural activities on clay soils in southern Britain. In its native areas, A. cotula thrives in temperate to Mediterranean climates, favoring poor, disturbed soils such as those in arable fields and waste grounds, and occurs at elevations ranging from to about 1500 meters. This elevational tolerance contributes to its widespread occurrence across varied terrains within the native range.

Introduced ranges and habitat preferences

Anthemis cotula has been introduced to various regions outside its native Mediterranean range, including North and South America, Australia, New Zealand, southern Africa, and parts of Asia such as India and Japan. In North America, it was first reported in 1841, likely arriving as a contaminant in crop seeds and forage shipments, with the first record in the Pacific Northwest of the United States in 1877. The species has since naturalized widely across the continent, from Canada to Mexico, and in South America, including Argentina. In the Southern Hemisphere, introductions to Australia and New Zealand occurred similarly through agricultural trade, with early records dating back to the mid-19th century. Southern Africa, particularly South Africa, also hosts established populations, while in Asia, it appeared in India around 50 years ago and is noted in Japan as an invasive species. As of 2025, it continues to spread in subtropical regions, with recent reports of increased prevalence in parts of Southeast Asia. In introduced ranges, A. cotula thrives in disturbed habitats such as roadsides, agricultural fields, waste areas, and overgrazed pastures, where it acts as a on bare or compacted ground. It prefers neutral to alkaline soils with a range of 6 to 8, though it can tolerate slightly acidic conditions, and requires full sun exposure for optimal growth and germination. The plant is drought-tolerant once established, relying on its system to access deeper , but it avoids shaded environments and poorly drained, waterlogged sites that promote rot. This weed demonstrates broad environmental adaptations, tolerating temperatures from -10°C to 35°C, which enables its persistence in temperate to subtropical climates across introduced areas. Its rapid and on exposed facilitate quick colonization of disturbed sites, often forming dense stands within a single season.

Ecology

Ecological interactions

Anthemis cotula attracts a range of generalist insect pollinators, primarily hoverflies (Syrphidae) and bees, which visit its flowers for nectar and pollen rewards. These insects facilitate both self- and cross-pollination, with the plant exhibiting variable reproductive strategies depending on pollinator availability in its habitat. Solitary bees and Lepidoptera also contribute to pollination, supporting the species' reproduction in disturbed agroecosystems. The plant experiences limited herbivory due to its strong unpleasant and low , which deter most herbivores. Few specialist , such as caterpillars of certain moths, feed on it, while generalist grazers like rabbits occasionally consume foliage but avoid heavy browsing owing to the plant's acrid taste and potential . This reduced herbivory allows A. cotula to persist in grazed areas where more palatable species are preferentially consumed. Endophytic microbes, including bacteria such as and species, colonize seeds, roots, and leaves of A. cotula, enhancing its ecological fitness. These bacteria promote nutrient uptake through mechanisms like phosphate solubilization (up to 80.7 μg/ml by Bacillus safensis) and ammonia production, while fungal endophytes like Alternaria alternata provide biocontrol against pathogens such as Fusarium oxysporum (up to 44.6% inhibition). Recent studies indicate that seed-associated consortia, dominated by (21% of isolates) and (15%), improve stress tolerance by protecting seedlings from infections like Botrytis cinerea (up to 55.7% inhibition). Root exudates of A. cotula exhibit allelopathic potential, releasing compounds such as terpenoids and that inhibit germination and growth of neighboring plants like Conyza canadensis and . Non-native populations produce unique profiles with 25% higher richness, supporting the novel weapons hypothesis for competitive suppression. These exudates also alter soil microbial communities by recruiting beneficial bacteria or disrupting native signaling, thereby reshaping dynamics to favor the plant's establishment.

Role in ecosystems

In its native range across and parts of , Anthemis cotula functions as a , readily colonizing disturbed grasslands and waste areas to initiate early succession processes. Its rapid growth and prolific seed production allow it to establish quickly on bare or compacted soils, where its helps stabilize soil particles and prevent during initial recovery phases. Additionally, the plant provides valuable for pollinators, attracting syrphid flies and other that visit its daisy-like flowers, thereby supporting early-season and pollen resources in successional habitats. Anthemis cotula contributes to cycling in native ecosystems through its , with above-ground decomposing to return to the upon . While it can accumulate moderate levels of in its tissues consistent with its preference for medium- soils (Ellenberg N value 5.6), this role remains minor compared to leguminous species, as it lacks nitrogen-fixing symbionts. In native areas, Anthemis cotula supports through specific microbial symbioses, such as seed endophytes that may aid without dominating long-term . As an , Anthemis cotula plays a limited role in due to its short lifespan and relatively low accumulation, though it contributes modestly to in disturbed patches. Ecologically, it serves as an indicator of disturbed, moderately dry conditions with intermediate availability, signaling areas of disruption and potential for .

Invasiveness

History of spread

Anthemis cotula, native to the Mediterranean region of , was first introduced to in the early 19th century, likely as a contaminant in shipments of seeds and , with the earliest record dating to 1841. It may also have been intentionally introduced by settlers, including figures like , who planted it during his travels in the early 1800s believing it possessed antimalarial properties. By the mid-19th century, the plant had established in eastern states such as and began spreading westward through agricultural expansion. The primary vectors of its global spread included contaminated agricultural seeds, forage, ship ballast, and imports associated with wool and crop trade, facilitating its dispersal during periods of European colonization and intensified farming. Human activities, particularly the transport of goods via maritime routes and the establishment of colonial agriculture, accelerated its introduction to new continents, where it thrived in disturbed soils. In Australia, it arrived via these pathways and was first recorded in 1873, becoming naturalized in southeastern regions shortly thereafter. Similarly, in India, initial records date to 1972, driven by agricultural disturbances. Key milestones in its spread include its rapid proliferation in the farmlands by 1900, where it became a common weed in crops due to ongoing contamination and farm machinery movement. In the of the U.S., it was documented by 1877 and has persisted in agricultural systems for over 140 years. More recently, in the Kashmir Himalaya of , populations have expanded significantly since 2000, following its initial detection there in 1972, driven by further agricultural disturbances. This pattern underscores the role of European colonial agriculture in promoting its worldwide dissemination.

Mechanisms and impacts

Anthemis cotula exhibits high , enabling it to adapt rapidly to diverse environmental conditions through variations in traits such as growth rate and , which facilitate its in disturbed habitats like agricultural fields and roadsides. This , combined with rapid growth and a protracted recruitment pattern peaking in autumn and spring, allows the species to outpace native competitors and exploit seasonal opportunities. Furthermore, low observed in invaded populations is offset by the persistence of banks, which maintain propagule viability and support long-term population resilience despite reduced variability. Recent metabolomic studies have revealed in volatile compounds (VOCs), with invasive populations in non-native ranges producing defensive profiles, such as higher sesquiterpenes and monoterpenes, that deter herbivores and pathogens more effectively than in native Mediterranean counterparts. This chemical contributes to invasion success by improving and competitive ability across cycles and elevations. Additionally, seed endophytes play a crucial role in enhancing , with over 75% of isolated strains from non-native seeds demonstrating -promoting activities, including improved uptake and resistance, thereby aiding expansion into novel habitats. In invaded sites, A. cotula significantly alters properties, increasing available and by 30–60% while shifting toward neutrality and reducing microbial diversity in invaded plots compared to uninvaded ones, as documented in studies from the Himalaya. These changes enhance cycling in favor of the invader but disrupt native soil biota and long-term ecosystem fertility. The invasive spread of A. cotula leads to substantial ecological and economic impacts, including outcompetition of in grasslands and reduced in sensitive regions like the , where it forms dense monocultures that suppress local flora. In , it causes yield reductions in crops such as peas, with losses up to 50% in heavily infested fields due to competition for resources and allelopathic effects. Economically, as a widespread in U.S. grain and forage systems, it imposes significant costs through diminished harvest quality and increased management needs, contributing to broader burdens estimated in billions annually. Genetic analyses of invaded populations indicate bottlenecks resulting in lower compared to native ranges, yet adaptability is preserved through epigenetic and phenotypic variation, allowing sustained despite founder effects.

Toxicity

Chemical compounds

Anthemis cotula contains several bioactive chemical compounds, with s serving as primary toxins. The most notable is anthecotulide, an allergenic responsible for , extracted from aerial parts at yields of 0.7% w/w dry weight, though concentrations can reach up to 7.3% in some populations. Coumarins are present in high amounts, contributing to the plant's , alongside other s such as anthecotulide-5,6-oxide (yield 2 mg) and 6-hydroxy-4,5-dehydro-5,6-dihydroanthecotuloide (yield 3.7 mg), isolated from aerial parts. These toxins are concentrated in leaves and flowers, typically at 0.1–1% dry weight across plant parts. Essential oils, responsible for the plant's characteristic , comprise sesquiterpenes and monoterpenes, with yields of 0.05–0.16% v/w from hydrodistillation of flowers and leaves. Key components include α-bisabolol (68.2–75.1%), (2.88–7.2%), β-farnesene (1.1–3.6%), bisabolol oxide A (0.88–3.2%), and spathulenol (1.18–3.1%), identified via GC-MS analysis. such as and hispidulin, along with phenolic acids like , are also prominent, particularly in flowers (up to 77.53% of extract ) and leaves. These compounds are biosynthesized primarily in glandular trichomes, typical of the tribe, where terpenoids like proazulene precursors to are produced. (VOC) profiles vary by growth stage and organ, with higher diversity (up to 143 VOCs) and ester content in winter annuals during reproductive phases, compared to terpene-dominated summer annuals; flowers exhibit elevated esters and sesquiterpenes relative to leaves and roots. Analytical methods such as GC-MS for essential oils and LC-ESI-MS/MS for phenolics have confirmed these compositions in recent studies.

Effects on organisms

Anthemis cotula, commonly known as stinking chamomile or mayweed, exhibits toxicity primarily through its sesquiterpene lactones and volatile oils (e.g., containing bisabolol and chamazulene), which can affect various organisms upon contact or ingestion. In livestock such as cattle, horses, and goats, ingestion leads to low-level irritation of skin and mucous membranes, resulting in symptoms like rashes, mouth blistering, soreness, and diarrhea; the plant's strong odor and taste often deter grazing, reducing severe cases, though it can taint dairy milk with an unpleasant flavor. For companion animals, including dogs and cats, exposure causes , vomiting, anorexia, and allergic reactions, with prolonged ingestion potentially leading to bleeding tendencies due to the cumulative effects of its irritant compounds. In , similar irritant effects have been reported, though the plant is generally avoided. Humans experience primarily dermatological effects from handling the plant, such as characterized by skin inflammation and rashes, attributed to sesquiterpene lactones like anthecotulide and ; rare cases of severe have occurred following ingestion, often via contamination of tea, with symptoms including systemic allergic responses and cross-reactivity to other pollens. On plants, A. cotula demonstrates allelopathic potential through and extracts that inhibit and seedling growth in neighboring species, such as Conyza canadensis and , via chemical interference that disrupts community structure and favors its invasiveness. Ecologically, while unpalatable to most herbivores, its flowers attract generalist pollinators, potentially altering dynamics in invaded habitats, though overall it reduces native by outcompeting forage species.